Comparison of different liquid anaerobic digestion effluents as inocula and nitrogen sources for solid-state batch anaerobic digestion of corn stover

Effluents from three liquid anaerobic digesters, fed with municipal sewage sludge, food waste, or dairy waste, were evaluated as inocula and nitrogen sources for solid-state batch anaerobic digestion of corn stover in mesophilic reactors. Three feedstock-to-effluent (F/E) ratios (i.e., 2, 4, and 6) were tested for each effluent. At an F/E ratio of 2, the reactor inoculated by dairy waste effluent achieved the highest methane yield of 238.5 L/kgVS_feed, while at an F/E ratio of 4, the reactor inoculated by food waste effluent achieved the highest methane yield of 199.6 L/kgVS_feed. The microbial population and chemical composition of the three effluents were substantially different. Food waste effluent had the largest population of acetoclastic methanogens, while dairy waste effluent had the largest populations of cellulolytic and xylanolytic bacteria. Dairy waste also had the highest C/N ratio of 8.5 and the highest alkalinity of 19.3 g CaCO₃/kg. The performance of solid-state batch anaerobic digestion reactors was closely related to the microbial status in the liquid anaerobic digestion effluents.     

环境条件对浮游藻色素特征的影响及应用研究进展

基于色素分析的浮游藻化学分类方法已经成为从宏观上对浮游藻群落组成和丰度进行定量研究的良好工具。浮游藻化学分类方法的应用需要对藻类色素特征及其在不同环境条件下的变化特点有较充分的了解。本文对在实验室培养条件下,光照和营养盐条件对不同藻种单位细胞色素含量、特征色素对叶绿素a比值的色素特征的影响,以及在淡水、高浑浊河口环境下,多种因素的综合作用、非藻类色素引起的误差等因素的研究进展进行了综述,并阐述了相关应用、存在的问题及未来的展望。     

浅谈钢制氮封储罐泄漏防治措施

从消除储罐泄漏点、加强日常管理方面阐述了如何做好氮封储罐泄漏治理与预防,并对加强储罐泄漏防治提出建议。     

How much real cost has China paid for its economic growth?

China’s economic growth has a serious impact on the environment and resources. How much real cost did China pay for its economic growth? This paper estimates the monetary costs of resource depletion, environmental pollution, and ecological degradation. The paper examines the geographic distribution of resource and environmental losses across 31 provinces. The findings allow us to reach the following conclusions. First, the national cost of resource depletion, environmental pollution, and ecological degradation in 2005 was 2.5 trillion RMB. It accounted for 13.5% of China’s gross domestic product (GDP). Secondly, the cost of resource depletion, ecological degradation, and environmental pollution has a different spatial distribution. The cost of resources depletion mainly distributes in the central area, the cost of environmental pollution is in the eastern area, and the cost of ecological degradation lies in the western area. Thirdly, the cost of natural resources depletion is 1,672.5 billion RMB, accounting for 67.8% of the total cost of resource and environment. It indicates that economic development has a high cost of resource depletion.     

Effect of methylmercury on LPO levels, SH groups and activities of GSH-Px, SOD, XOD in liver of rats

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